CN105236661A - System and method for preparing ultrapure water with zero wastewater discharge - Google Patents

System and method for preparing ultrapure water with zero wastewater discharge Download PDF

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Publication number
CN105236661A
CN105236661A CN201510779129.1A CN201510779129A CN105236661A CN 105236661 A CN105236661 A CN 105236661A CN 201510779129 A CN201510779129 A CN 201510779129A CN 105236661 A CN105236661 A CN 105236661A
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water
tank
subsystem
storage tank
filter
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CN105236661B (en
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尚通明
王自伟
刘维桥
何沁华
魏成文
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Liyang Lifang Precious Metals Material Co ltd
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Jiangsu University of Technology
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Priority to CN201711048677.2A priority patent/CN107804943B/en
Priority to CN201510779129.1A priority patent/CN105236661B/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/048Purification of waste water by evaporation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/44Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
    • C02F1/441Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/42Treatment of water, waste water, or sewage by ion-exchange
    • C02F2001/427Treatment of water, waste water, or sewage by ion-exchange using mixed beds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/02Non-contaminated water, e.g. for industrial water supply
    • C02F2103/04Non-contaminated water, e.g. for industrial water supply for obtaining ultra-pure water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/124Water desalination
    • Y02A20/131Reverse-osmosis

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Treatment Of Water By Ion Exchange (AREA)

Abstract

The invention discloses a system for preparing ultrapure water without wastewater discharge, which comprises a pretreatment subsystem, a desalination subsystem, a fine treatment subsystem and a regenerated wastewater pretreatment subsystem; the pretreatment subsystem comprises a raw water storage tank, a water pump, a softening filter, a pH value adjusting tank, a quartz sand filter, an activated carbon filter, a zeolite filter and a pretreatment water storage tank which are sequentially connected through pipelines, the desalination subsystem comprises a primary reverse osmosis host and a secondary reverse osmosis host, the fine treatment subsystem is a mixed bed system, and the regeneration wastewater pretreatment subsystem comprises a regeneration wastewater neutralization pond and an evaporation crystallization device. The system and the method for preparing the ultrapure water realize zero emission of wastewater in the ultrapure water preparation process; the system for preparing ultrapure water comprises a mixed bed, and a large amount of acid-base wastewater generated in the regeneration of the cation resin and the anion resin in the mixed bed is not discharged into a sewage pipe network as in the conventional treatment mode, but is treated in the system of the invention, and finally ultrapure water is obtained.

Description

The system and method preparing ultrapure water of no effuent discharge
Technical field
The present invention relates to a kind of preparation method of pure water, be specifically related to a kind of system and method preparing ultrapure water of production process no effuent discharge.
Background technology
Water is a kind of modal compound, and it is Source of life, is also the indispensable valuable source of modern industry.Along with the development of science and technology, the requirement of many fields to quality is more and more higher, and pure water preparation technology becomes a popular research field.
Pure water is divided into drinking pure and industrial pure water.Industrial pure water is divided into three kinds according to specific conductivity, as shown in table 1 below.
Table 1 industrial pure water classification (25 DEG C)
Ultrapure water is widely used in numerous industrial circles such as electronics, medicine, electric power, chemical industry as the analysis design mothod water of high-quality, production technique water and boiler plant supply water.It not only has direct relation with the quality of product and yield rate, and produces active influence to the development of industry-by-industry, is one of starting material indispensable in production process.
About the preparation method of ultrapure water, the female grade of Zhang Zhi is at " ultrapure water preparation " (modern chemical industry, 2011,04 phase: 79-82) mention in a literary composition and prepare ultrapure water with the technical process process petro-chemical corporation underground water of pre-treatment+two-pass reverse osmosis+electrodeionization EDI+ polishing essence mixed bed.In literary composition using quartz filter and accurate filter as pre-treatment, remove the suspended substance in former water, colloid, colourity, turbidity, organism etc., first-stage reverse osmosis, as pro desalting device, removes most dissolved salts, particle, hardness, activated silica in water; Two-pass reverse osmosis and electrodeionization, as smart desalting plant, remove the dissolved salts of trace in water, hardness and SiO further 2, make the effluent quality of whole system reach the requirement of ultrapure water effluent quality; Electrodeionization EDI and polishing essence mixed bed are as the 3rd cover operation, and main triple guaranteeing role, ensures that effluent quality meets associated gas washing water quality needs.This technological work dependable performance, water production rate are 3 tons/h, stable effluent quality, produce water resistance rate at 0.056 below μ S/cm, meet the standard of industrial extra-pure water, and the regeneration period of polishing essence mixed bed extends greatly, decreases component environment and pollutes.But this technique needs to use EDI device, the initial investment of EDI device is expensive, keep in repair more difficult, a lot of material and accessory all require import, and initial investment is very expensive, be not suitable for medium and small sized enterprises, and EDI is when water power is from MODE of operation, the efficiency of electric energy and desalination is lower.
Such as Chinese patent literature CN104150663A(application number 201410438809.2 again) disclose a kind of ultrapure water production system, comprise preprocessing subsystem, reverse osmosis subsystem, mixed bed subsystem; Described preprocessing subsystem comprises the raw water box, raw water pump, more medium filter, activated charcoal filter, the cartridge filter that are connected successively; Described reverse osmosis subsystem comprises one-level high-pressure pump, RO reverse osmosis system, RO water tank, secondary high-pressure pump, pure water tank, and described RO reverse osmosis system comprises first-stage reverse osmosis main frame, two-pass reverse osmosis main frame; Described mixed bed subsystem comprises pure water pump, mixed bed, ultraviolet sterilizer, accurate filter, and pure water tank is connected with pure water pump, and pure water pump, mixed bed, ultraviolet sterilizer, accurate filter connect successively.
All employ mixed bed in above-mentioned ultrapure water preparation technology, need frequent soda acid to regenerate in mixed bed operational process, produce a large amount of acid-base waste fluid, in above-mentioned document, do not mention the treatment process of acid-base waste fluid; The process of the acidic and alkaline waste water that current mixed bed regeneration produces is discharged into municipal wastewater pipe network after being neutralized, and this processing mode is also the waste of water resources.
In recent years; along with people economize on resources and the improving constantly of environmental protection consciousness; what not only require water quality can meet each field uses water requirement; also will some cause the technical matters of water resource waste and contaminate environment to be improved to preparing in ultrapure water technique, these have all promoted the development of pure water preparation technology.
Summary of the invention
Technical problem to be solved by this invention is to provide a kind of system and method preparing ultrapure water of production process no effuent discharge.
The technical scheme realizing the present invention first object is a kind of system preparing ultrapure water of no effuent discharge, comprises preprocessing subsystem, desalination subsystem, precision processing subsystem and regenerative wastewater preprocessing subsystem.
Described preprocessing subsystem comprises the former water storage tank, water pump, softening filter, pH value regulating tank, quartz filter, activated charcoal filter, zeolite filter and the pretreated water storage tank that are connected successively by pipeline.
Desalination subsystem comprises the first high-pressure pump, first-stage reverse osmosis main frame, reverse osmosis water tank, the second high-pressure pump, two-pass reverse osmosis main frame, ultraviolet sterilizer, accurate filter and the de-salted water storage tank that are connected successively by pipeline, and the water-in of the first high-pressure pump is connected with the water outlet of the pretreated water storage tank of preprocessing subsystem.
Precision processing subsystem is mixed-bed system, comprise force (forcing) pump, 2 groups of hybrid ionic exchange columns and ultrapure water storage tank, the water-in of force (forcing) pump is connected by the water outlet of pipeline with the de-salted water storage tank of desalination subsystem, the water outlet of force (forcing) pump and the water-in of mixed bed are by pipeline communication, and the water outlet of mixed bed is connected with ultrapure water storage tank by pipeline.
Regenerative wastewater preprocessing subsystem comprises regenerative wastewater neutralization tank and evaporated crystallization device, described evaporation unit is provided with condensation water collection pipeline and water of condensation storage tank, the water outlet of water of condensation storage tank is connected with the softening filter of preprocessing subsystem with pipeline by water pump, and pipeline is provided with valve; Wherein the regeneration acid solution outlet of the hybrid ionic exchange column of precision processing subsystem passes in regenerative wastewater neutralization tank by pipeline, the outlet of regeneration alkali lye also passes in regenerative wastewater neutralization tank by pipeline, and waste water in pond is delivered in evaporation unit by water pump and pipeline by the water outlet of regenerative wastewater neutralization tank.
The pH value regulating tank of described preprocessing subsystem comprises can body, acid solution tank and alkali liquid tank, and acid solution tank and alkali liquid tank are arranged on the top of can body, and acid solution tank and alkali liquid tank are respectively by pipeline and can body UNICOM, and pipeline is provided with valve; Can body is also provided with pH value detector, and the electrode of pH value detector is immersed in the liquid in pH value regulating tank, the instant pH value reading measurement pot liquid; Store the hydrochloric acid of 20% ~ 30% in acid solution tank, in alkali liquid tank, store the sodium hydroxide solution of 15% ~ 20%.
The shaft of the hybrid ionic exchange column of described precision processing subsystem is provided with the import of regeneration acid solution, the outlet of regeneration acid solution, the import of regeneration alkali lye, the outlet of regeneration alkali lye; The import of regeneration acid solution is connected with hydrochloric acid tank by pipeline, the import of regeneration alkali lye is connected with sodium hydroxide solution storage tank by pipeline, wherein in hydrochloric acid tank, the concentration of hydrochloric acid is 20% ~ 30%, and in sodium hydroxide solution storage tank, the concentration of sodium hydroxide solution is 15% ~ 20%.
The processing load of preprocessing subsystem is 8 ~ 12 times of desalination subsystem processes load, and the processing load of preprocessing subsystem is 8 ~ 12 times of the processing load of precision processing subsystem.
The technical scheme realizing the present invention second object is a kind of method preparing ultrapure water of no effuent discharge, comprises the following steps:
1. treating nature water; Passed in former water storage tank by former water, open water pump, former water, by softening filter, removes scale-forming ion in water, reduces original water hardness; The water flowed out from softening filter enters in pH value regulating tank, pH value detector reads the pH value of water in tank in time, if the pH value of water is greater than 7.0 in tank, in tank, drip hydrochloric acid to pH value reading is 7.0, if the pH value of water is less than 7.0 in tank, in tank, drip sodium hydroxide solution to pH value reading is 7.0, if the pH value of water is 7.0 in tank, does not need to regulate.
The water that pH value is adjusted to 7.0 flows out from pH value regulating tank, successively through quartz filter, activated charcoal filter and zeolite filter, through this three-stage filtration except suspended solid, colloid, the organism of 1 ~ 20 μm in anhydrating, alleviate follow-up reverse osmosis membrane processing load, the water flowed out from zeolite filter is stored in pretreated water storage tank.
2. desalting treatment; Water in pretreated water storage tank is delivered in first-stage reverse osmosis main frame by the first high-pressure pump of desalination subsystem, removes most dissolved salts, particle, hardness and activated silica in water through first-stage reverse osmosis; Water through first-stage reverse osmosis process carries out two-pass reverse osmosis again, removes the dissolved salts of trace in water, hardness and SiO further 2.
Water through two steps ro process is sent in ultraviolet sterilizer, the nucleic acid function of ultraviolet damage organism and make bacterial death; The water that ultraviolet sterilizer flows out enters in accurate filter, and the bacterium in water is removed, and the water flowed out from accurate filter is stored in de-salted water storage tank.
3. precision processing; Water after step 2. desalting treatment is delivered in mixed bed by the force (forcing) pump of precision processing subsystem, and in mixed bed, the degree of depth removes the mineral substance in water, and the specific conductivity of effluent quality reaches the standard of ultrapure water, and the ultrapure water obtained is stored in ultrapure water storage tank.
4. mixed bed regeneration waste liquid process; Be disposed after 100 ~ 150 tons of former water continuously, after anionite-exchange resin in mixed bed and Zeo-karb use hydrochloric acid and sodium hydroxide to regenerate respectively, to regeneration waste liquid pre-treatment, the spent acid and the waste lye that are about to regeneration pass in the regenerative wastewater neutralization tank of regenerative wastewater preprocessing subsystem, heat in neutralization tank He in rear feeding evaporated crystallization device, along with the rising of salt concn in evaporated crystallization device, sodium-chlor is separated out, collect the sodium-chlor of crystallization, be stored in after the water vapor condensation produced in evaporative process in water of condensation storage tank.
After pre-treatment, the water in water of condensation storage tank is sent into and is prepared in the softening filter of the preprocessing subsystem of ultrapure water system, 1. 3. carries out purifying to step obtain ultrapure water according to above-mentioned steps.
Concrete, after pre-treatment, the water in water of condensation storage tank enters in pH value regulating tank from the water that softening filter flows out, and pH value detector reads the pH value of water in tank, and the pH of water in pH value regulating tank is adjusted to 7.0; The water that pH value is adjusted to 7.0 flows out from pH value regulating tank, successively through quartz filter, activated charcoal filter and zeolite filter, through this three-stage filtration except suspended solid, colloid, the organism in anhydrating, the water flowed out from zeolite filter is stored in pretreated water storage tank; Water in pretreated water storage tank is delivered in first-stage reverse osmosis main frame by the first high-pressure pump of desalination subsystem, and the water through first-stage reverse osmosis process carries out two-pass reverse osmosis again; Enter after two steps ro in ultraviolet sterilizer, the nucleic acid function of ultraviolet damage organism and make bacterial death; The water that ultraviolet sterilizer flows out enters in accurate filter, and the bacterium in water is removed, and the water flowed out from accurate filter is stored in de-salted water storage tank; Water after desalting treatment is delivered in mixed bed by the force (forcing) pump of precision processing subsystem, and in mixed bed, the degree of depth removes the mineral substance in water, and mixed bed goes out the standard that electrical conductivity of water reaches ultrapure water.
The processing load of above-mentioned steps 1. treating nature water is 8 ~ 12 times of step 2. desalting treatment load, and the processing load of step 1. treating nature water is 8 ~ 12 times of step 3. precision processing load.
The present invention has positive effect: (1) system and method preparing ultrapure water of the present invention achieves ultrapure water preparation process wastewater zero discharge; The system preparing ultrapure water comprises mixed bed, and a large amount of acidic and alkaline waste waters produced when the positive resin in mixed bed and negative resin regeneration are not be discharged in sewage network as existing processing mode, but are processed in the system of the present invention, and finally obtain ultrapure water.
(2) processing load preparing the preprocessing subsystem of the system of ultrapure water of the present invention is 8 ~ 12 times of the processing load of follow-up desalination subsystem and precision processing subsystem, the water quality entering reverse osmosis unit is improve through pretreated water, alleviate the operating pressure of reverse osmosis membrane, reduce fouling membrane, and larger portative power ensures that native system can process comparatively pure tap water, the reuse water of mixed bed simultaneously, 2 μ s/cm can be reached through pretreated middle electrical conductivity of water, can directly use as domestic water.
Because the preprocessing subsystem before precision processing subsystem and desalination subsystem are to the process of former water, the regeneration period of mixed-bed resin is elongated, and the process water yield reaches 120 tons and just need regenerate the yin and yang resin of mixed bed.
(3) system and method preparing ultrapure water of the present invention does not use expensive device, and treatment facility input cost is lower, and occupation area of equipment is little, is applicable to medium and small sized enterprises' manufacture ultrapure water.
(4) the ultrapure electrical conductivity of water that prepared by the system and method preparing ultrapure water of the present invention is low to moderate 0.02 μ s/cm.
Accompanying drawing explanation
Fig. 1 is process flow sheet of the present invention.
Embodiment
(system preparing ultrapure water of embodiment 1, no effuent discharge)
See Fig. 1, the system preparing ultrapure water of the no effuent discharge of the present embodiment comprises preprocessing subsystem, desalination subsystem, precision processing subsystem and regenerative wastewater preprocessing subsystem.
Described preprocessing subsystem comprises the former water storage tank, water pump, softening filter, pH value regulating tank, quartz filter, activated charcoal filter, zeolite filter and the pretreated water storage tank that are connected successively by pipeline.
Wherein pH value regulating tank comprises can body, acid solution tank and alkali liquid tank, and acid solution tank and alkali liquid tank are arranged on the top of can body, and acid solution tank and alkali liquid tank are respectively by pipeline and can body UNICOM, and pipeline is provided with valve.Can body is also provided with pH value detector, and the electrode of pH value detector is immersed in the liquid in pH value regulating tank, measures the pH value of pot liquid at any time.Store the hydrochloric acid of 20% ~ 30% in acid solution tank, in alkali liquid tank, store the sodium hydroxide solution of 15% ~ 20%.
Described desalination subsystem comprises the first high-pressure pump, first-stage reverse osmosis main frame, reverse osmosis water tank, the second high-pressure pump, two-pass reverse osmosis main frame, ultraviolet sterilizer, accurate filter and the de-salted water storage tank that are connected successively by pipeline.The water-in of the first high-pressure pump is connected with the water outlet of the pretreated water storage tank of preprocessing subsystem.
Precision processing subsystem is mixed-bed system, comprises force (forcing) pump, hybrid ionic exchange column (abbreviation mixed bed) and ultrapure water storage tank that 2 groups of diameters are 600mm; The water-in of force (forcing) pump is connected by the water outlet of pipeline with the de-salted water storage tank of desalination subsystem, and the water outlet of force (forcing) pump and the water-in of mixed bed are by pipeline communication, and the water outlet of mixed bed is connected with ultrapure water storage tank by pipeline.
The shaft of mixed bed is provided with the import of regeneration acid solution, the outlet of regeneration acid solution, the import of regeneration alkali lye, the outlet of regeneration alkali lye; The import of regeneration acid solution is connected with hydrochloric acid tank by pipeline, and the import of regeneration alkali lye is connected with sodium hydroxide solution storage tank by pipeline, and wherein the concentration of hydrochloric acid is 20% ~ 30%, and the concentration of sodium hydroxide solution is 15% ~ 20%.
Regenerative wastewater preprocessing subsystem comprises regenerative wastewater neutralization tank and evaporated crystallization device, and described evaporation unit is provided with condensation water collection pipeline and water of condensation storage tank.The regeneration acid solution outlet of mixed bed passes in regenerative wastewater neutralization tank by pipeline, the outlet of regeneration alkali lye also passes in regenerative wastewater neutralization tank by pipeline, and the sodium chloride solution of neutralized wastewater and high density is delivered in evaporation unit by water pump and pipeline by the water outlet of regenerative wastewater neutralization tank.Waste water after neutralization heating evaporation in evaporation unit, the water of condensation obtained after the vapor condensation of generation is stored in water of condensation storage tank through condensing water conduit.The water outlet of water of condensation storage tank is connected with the softening filter of preprocessing subsystem with pipeline by water pump, and pipeline is provided with valve.
Appeal no effuent discharge prepare in the system of ultrapure water, the processing load of preprocessing subsystem is 8 ~ 12 times of the processing load of follow-up desalination subsystem and precision processing subsystem; In the present embodiment, the processing load of preprocessing subsystem is 5 tons/h, and the processing load of desalination subsystem and precision processing subsystem is 0.5 ton/h.
(method preparing ultrapure water of embodiment 2, no effuent discharge)
The former water of the present embodiment process is tap water, and specific conductivity is 400 ~ 500 μ s/cm.
The method preparing ultrapure water of the no effuent discharge of the present embodiment uses the system described in embodiment 1, comprises the following steps during process:
1. treating nature water.Passed in former water storage tank by tap water, open water pump, former water, by softening filter, removes the scale-forming ion such as calcium, magnesium in water, reduces original water hardness; The water flowed out from softening filter enters in pH value regulating tank, pH value detector reads the pH value of water in tank in time, if the pH value of water is greater than 7.0 in tank, in tank, drip hydrochloric acid to pH value reading is 7.0, if the pH value of water is less than 7.0 in tank, in tank, drip sodium hydroxide solution to pH value reading is 7.0, if the pH value of water is 7.0 in tank, does not need to regulate.
The water that pH value is adjusted to 7.0 flows out from pH value regulating tank, successively through quartz filter, activated charcoal filter and zeolite filter, through this three-stage filtration except the suspended solid, colloid, organism etc. of 1 ~ 20 μm in anhydrating, alleviate follow-up reverse osmosis membrane processing load.The water flowed out from zeolite filter is stored in pretreated water storage tank, and the middle electrical conductivity of water 1. processed through step is 2 μ s/cm.
Processing load during treating nature water is 5 tons/h.
2. desalting treatment.Water in pretreated water storage tank is delivered in first-stage reverse osmosis main frame by the first high-pressure pump of desalination subsystem, removes most dissolved salts, particle, hardness and activated silica in water through first-stage reverse osmosis; Water through first-stage reverse osmosis process carries out two-pass reverse osmosis again, removes the dissolved salts of trace in water, hardness and SiO further 2.
Pretreated water enters in ultraviolet sterilizer after two steps ro, the nucleic acid function of ultraviolet damage organism and make bacterial death; The water that ultraviolet sterilizer flows out enters in accurate filter, and the bacterium in water is removed, and the water flowed out from accurate filter is stored in de-salted water storage tank.
Step processing load is 2. 0.5 ton/h.
Electrical conductivity of water through step 2. desalting treatment is 0.2 ~ 0.3 μ s/cm.
3. precision processing.Water after step 2. desalting treatment is delivered in mixed bed by the force (forcing) pump of precision processing subsystem, in mixed bed, the degree of depth removes the mineral substance in water, the specific conductivity of effluent quality is made to reach 0.02 μ s/cm, reach the standard (0.055 ~ 0.1 μ s/cm) of ultrapure water, the ultrapure water obtained is stored in ultrapure water storage tank stand-by or for sale.
Step processing load is 3. 0.5 ton/h, and the processing load of a complete set of equipment is 0.5 ton/h.
4. mixed bed regeneration waste liquid process.It is 120 that the present embodiment is disposed in 100 ~ 150(the present embodiment continuously) after the former water of ton, anionite-exchange resin in mixed bed and Zeo-karb need regeneration, according to existing renovation process, use hydrochloric acid and sodium hydroxide respectively to after two kinds of resin regenerations, first to regenerative wastewater pre-treatment, spent acid and the waste lye of regeneration pass in the regenerative wastewater neutralization tank of regenerative wastewater preprocessing subsystem, heat in neutralization tank He in rear feeding evaporated crystallization device, along with the rising of salt concn in evaporated crystallization device, sodium-chlor is separated out, collect the sodium-chlor of crystallization, be stored in water of condensation storage tank after the water vapor condensation produced in evaporative process, condensation electrical conductivity of water is 800 μ s/cm.
After regenerative wastewater pre-treatment, water in water of condensation storage tank is sent in the softening filter of preprocessing subsystem, 1. 3. carries out purifying to step according to above-mentioned steps.
Concrete, after the water in water of condensation storage tank is sent into and softened in the softening filter of preprocessing subsystem, the water flowed out from softening filter enters in pH value regulating tank, and pH value detector reads the pH value of water in tank, and the pH of water in pH value regulating tank is adjusted to 7.0.
The water that pH value is adjusted to 7.0 flows out from pH value regulating tank, successively through quartz filter, activated charcoal filter and zeolite filter, through this three-stage filtration except the suspended solid, colloid, organism etc. in anhydrating, the water flowed out from zeolite filter is stored in pretreated water storage tank, and now electrical conductivity of water is 150 ~ 200 μ s/cm.
Water in pretreated water storage tank is delivered in first-stage reverse osmosis main frame by the first high-pressure pump of desalination subsystem, removes most dissolved salts, particle, hardness and activated silica in water through first-stage reverse osmosis; Water through first-stage reverse osmosis process carries out two-pass reverse osmosis again, removes the dissolved salts of trace in water, hardness and SiO further 2.
Pretreated water enters in ultraviolet sterilizer after two steps ro, the nucleic acid function of ultraviolet damage organism and make bacterial death; The water that ultraviolet sterilizer flows out enters in accurate filter, and the bacterium in water is removed, and the water flowed out from accurate filter is stored in de-salted water storage tank.
Water after desalting treatment is delivered in mixed bed by the force (forcing) pump of precision processing subsystem, and in mixed bed, the degree of depth removes the mineral substance in water, and mixed bed goes out electrical conductivity of water and reaches 0.03 μ s/cm, reaches the standard (0.055 ~ 0.1 μ s/cm) of ultrapure water equally.
Therefore the system and method preparing ultrapure water of the present invention achieves ultrapure water preparation process wastewater zero discharge; The system preparing ultrapure water comprises mixed bed, and a large amount of acidic and alkaline waste waters produced when the positive resin in mixed bed and negative resin regeneration are not be discharged in sewage network as existing processing mode, but are processed in the system of the present invention, and finally obtain ultrapure water.

Claims (7)

1. the system preparing ultrapure water of no effuent discharge, is characterized in that: comprise preprocessing subsystem, desalination subsystem, precision processing subsystem and regenerative wastewater preprocessing subsystem;
Described preprocessing subsystem comprises the former water storage tank, water pump, softening filter, pH value regulating tank, quartz filter, activated charcoal filter, zeolite filter and the pretreated water storage tank that are connected successively by pipeline;
Desalination subsystem comprises the first high-pressure pump, first-stage reverse osmosis main frame, reverse osmosis water tank, the second high-pressure pump, two-pass reverse osmosis main frame, ultraviolet sterilizer, accurate filter and the de-salted water storage tank that are connected successively by pipeline, and the water-in of the first high-pressure pump is connected with the water outlet of the pretreated water storage tank of preprocessing subsystem;
Precision processing subsystem is mixed-bed system, comprise force (forcing) pump, 2 groups of hybrid ionic exchange columns and ultrapure water storage tank, the water-in of force (forcing) pump is connected by the water outlet of pipeline with the de-salted water storage tank of desalination subsystem, the water outlet of force (forcing) pump and the water-in of mixed bed are by pipeline communication, and the water outlet of mixed bed is connected with ultrapure water storage tank by pipeline;
Regenerative wastewater preprocessing subsystem comprises regenerative wastewater neutralization tank and evaporated crystallization device, described evaporation unit is provided with condensation water collection pipeline and water of condensation storage tank, the water outlet of water of condensation storage tank is connected with the softening filter of preprocessing subsystem with pipeline by water pump, and pipeline is provided with valve; Wherein the regeneration acid solution outlet of the hybrid ionic exchange column of precision processing subsystem passes in regenerative wastewater neutralization tank by pipeline, the outlet of regeneration alkali lye also passes in regenerative wastewater neutralization tank by pipeline, and waste water in pond is delivered in evaporation unit by water pump and pipeline by the water outlet of regenerative wastewater neutralization tank.
2. the system preparing ultrapure water of no effuent discharge according to claim 1, it is characterized in that: the pH value regulating tank of preprocessing subsystem comprises can body, acid solution tank and alkali liquid tank, acid solution tank and alkali liquid tank are arranged on the top of can body, acid solution tank and alkali liquid tank are respectively by pipeline and can body UNICOM, and pipeline is provided with valve; Can body is also provided with pH value detector, and the electrode of pH value detector is immersed in the liquid in pH value regulating tank, the instant pH value reading measurement pot liquid; Store the hydrochloric acid of 20% ~ 30% in acid solution tank, in alkali liquid tank, store the sodium hydroxide solution of 15% ~ 20%.
3. the system preparing ultrapure water of no effuent discharge according to claim 1, is characterized in that: the shaft of the hybrid ionic exchange column of precision processing subsystem is provided with the import of regeneration acid solution, the outlet of regeneration acid solution, the import of regeneration alkali lye, the outlet of regeneration alkali lye; The import of regeneration acid solution is connected with hydrochloric acid tank by pipeline, the import of regeneration alkali lye is connected with sodium hydroxide solution storage tank by pipeline, wherein in hydrochloric acid tank, the concentration of hydrochloric acid is 20% ~ 30%, and in sodium hydroxide solution storage tank, the concentration of sodium hydroxide solution is 15% ~ 20%.
4. according to the system preparing ultrapure water of the no effuent discharge one of claims 1 to 3 Suo Shu, it is characterized in that: the processing load of preprocessing subsystem is 8 ~ 12 times of desalination subsystem processes load, the processing load of preprocessing subsystem is 8 ~ 12 times of the processing load of precision processing subsystem.
5. the system preparing ultrapure water of no effuent discharge as claimed in claim 1 prepares a method for ultrapure water, it is characterized in that comprising the following steps:
1. treating nature water; Passed in former water storage tank by former water, open water pump, former water, by softening filter, removes scale-forming ion in water, reduces original water hardness; The water flowed out from softening filter enters in pH value regulating tank, pH value detector reads the pH value of water in tank in time, if the pH value of water is greater than 7.0 in tank, in tank, drip hydrochloric acid to pH value reading is 7.0, if the pH value of water is less than 7.0 in tank, in tank, drip sodium hydroxide solution to pH value reading is 7.0, if the pH value of water is 7.0 in tank, does not need to regulate;
The water that pH value is adjusted to 7.0 flows out from pH value regulating tank, successively through quartz filter, activated charcoal filter and zeolite filter, through this three-stage filtration except suspended solid, colloid, the organism of 1 ~ 20 μm in anhydrating, alleviate follow-up reverse osmosis membrane processing load, the water flowed out from zeolite filter is stored in pretreated water storage tank;
2. desalting treatment; Water in pretreated water storage tank is delivered in first-stage reverse osmosis main frame by the first high-pressure pump of desalination subsystem, removes most dissolved salts, particle, hardness and activated silica in water through first-stage reverse osmosis; Water through first-stage reverse osmosis process carries out two-pass reverse osmosis again, removes the dissolved salts of trace in water, hardness and SiO further 2;
Water through two steps ro process is sent in ultraviolet sterilizer, the nucleic acid function of ultraviolet damage organism and make bacterial death; The water that ultraviolet sterilizer flows out enters in accurate filter, and the bacterium in water is removed, and the water flowed out from accurate filter is stored in de-salted water storage tank;
3. precision processing; Water after step 2. desalting treatment is delivered in mixed bed by the force (forcing) pump of precision processing subsystem, and in mixed bed, the degree of depth removes the mineral substance in water, and the specific conductivity of effluent quality reaches the standard of ultrapure water, and the ultrapure water obtained is stored in ultrapure water storage tank;
4. mixed bed regeneration waste liquid process; Be disposed after 100 ~ 150 tons of former water continuously, after anionite-exchange resin in mixed bed and Zeo-karb use hydrochloric acid and sodium hydroxide to regenerate respectively, to regeneration waste liquid pre-treatment, spent acid and the waste lye of regeneration pass in the regenerative wastewater neutralization tank of regenerative wastewater preprocessing subsystem, heat in neutralization tank He in rear feeding evaporated crystallization device, along with the rising of salt concn in evaporated crystallization device, sodium-chlor is separated out, collect the sodium-chlor of crystallization, be stored in water of condensation storage tank after the water vapor condensation produced in evaporative process;
After pre-treatment, the water in water of condensation storage tank is sent into and is prepared in the softening filter of the preprocessing subsystem of ultrapure water system, 1. 3. carries out purifying to step obtain ultrapure water according to above-mentioned steps.
6. the system preparing ultrapure water of no effuent discharge according to claim 5 prepares the method for ultrapure water, it is characterized in that: step is 4. after pre-treatment, water in water of condensation storage tank enters in pH value regulating tank from the water that softening filter flows out, pH value detector reads the pH value of water in tank, and the pH of water in pH value regulating tank is adjusted to 7.0; The water that pH value is adjusted to 7.0 flows out from pH value regulating tank, successively through quartz filter, activated charcoal filter and zeolite filter, through this three-stage filtration except suspended solid, colloid, the organism in anhydrating, the water flowed out from zeolite filter is stored in pretreated water storage tank; Water in pretreated water storage tank is delivered in first-stage reverse osmosis main frame by the first high-pressure pump of desalination subsystem, and the water through first-stage reverse osmosis process carries out two-pass reverse osmosis again; Enter after two steps ro in ultraviolet sterilizer, the nucleic acid function of ultraviolet damage organism and make bacterial death; The water that ultraviolet sterilizer flows out enters in accurate filter, and the bacterium in water is removed, and the water flowed out from accurate filter is stored in de-salted water storage tank; Water after desalting treatment is delivered in mixed bed by the force (forcing) pump of precision processing subsystem, and in mixed bed, the degree of depth removes the mineral substance in water, and mixed bed goes out the standard that electrical conductivity of water reaches ultrapure water.
7. the system preparing ultrapure water of no effuent discharge according to claim 5 prepares the method for ultrapure water, it is characterized in that: the processing load for the treatment of nature water is 8 ~ 12 times of desalting treatment load, the processing load for the treatment of nature water is 8 ~ 12 times of precision processing load.
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106219820A (en) * 2016-08-31 2016-12-14 江苏宏标科技有限公司 A kind of for power plant's soft brush treatment desalinating process
CN107043187A (en) * 2017-05-05 2017-08-15 谭振光 The natural excessively stream sterile purification device of natural mineral water production waste water reuse
CN109095653A (en) * 2018-09-11 2018-12-28 乐清市正鑫金属件有限公司 Utilize the method for well water Pure-water Making
CN111977850A (en) * 2020-08-24 2020-11-24 广东乐纯环保工程有限公司 Heavy metal wastewater reduction and concentration technology
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CN116102066A (en) * 2023-01-10 2023-05-12 陕西亿杰博顺环保科技有限公司 Method and system for preparing ammonium molybdate by self-circulation of molybdenum-containing high radon nitrogen wastewater

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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CN109516618A (en) * 2018-11-14 2019-03-26 中国电子工程设计院有限公司 Ultrapure water intelligent remote operational system
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CN113243470A (en) * 2021-05-27 2021-08-13 海南木辣达生物科技有限公司 Preparation method of honey beverage

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5470461A (en) * 1991-10-04 1995-11-28 Mitsubishi Denki Kabushiki Kaisha Apparatus for producing pure water
CN201362619Y (en) * 2009-01-22 2009-12-16 陈涛 Laboratory industrial ultrapure water purifier
CN201704140U (en) * 2010-04-27 2011-01-12 中国人民解放军第三军医大学第一附属医院 Integrated water treatment system
CN102531257A (en) * 2010-12-27 2012-07-04 J-美凯龙株式会社 Recycling device of inorganic wastewater and the recycling method of inorganic wastewater using the solar heat
CN202440393U (en) * 2011-07-12 2012-09-19 天津鑫惠诚环保科技发展有限公司 Electronic-grade ultrapure water system
CN103539288A (en) * 2013-10-31 2014-01-29 神华集团有限责任公司 Industrial wastewater recovery method and wastewater recovery system
CN204529569U (en) * 2015-01-23 2015-08-05 昆山广盛源水务科技有限公司 A kind of ultrapure water production system
CN204529568U (en) * 2015-01-23 2015-08-05 昆山广盛源水务科技有限公司 A kind of ultra-pure-water treatment system

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07155744A (en) * 1993-12-06 1995-06-20 Hitachi Ltd Production of ultrapure water
KR101121225B1 (en) * 2009-09-16 2012-03-23 주식회사 제이미크론 recycling device of inorganic wastewater and the recycling method of inorganic wastewater
CN203976546U (en) * 2014-05-30 2014-12-03 天津邦盛净化设备有限公司 Ultrapure water wastewater treatment equipment
CN104495980A (en) * 2014-11-19 2015-04-08 重庆中科过滤设备制造有限公司 Boiler water deionization treatment system
CN105016541B (en) * 2015-07-29 2017-04-26 凯姆德(北京)能源环境科技有限公司 Method for separating and recovering salts from high-salt wastewater

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5470461A (en) * 1991-10-04 1995-11-28 Mitsubishi Denki Kabushiki Kaisha Apparatus for producing pure water
CN201362619Y (en) * 2009-01-22 2009-12-16 陈涛 Laboratory industrial ultrapure water purifier
CN201704140U (en) * 2010-04-27 2011-01-12 中国人民解放军第三军医大学第一附属医院 Integrated water treatment system
CN102531257A (en) * 2010-12-27 2012-07-04 J-美凯龙株式会社 Recycling device of inorganic wastewater and the recycling method of inorganic wastewater using the solar heat
CN202440393U (en) * 2011-07-12 2012-09-19 天津鑫惠诚环保科技发展有限公司 Electronic-grade ultrapure water system
CN103539288A (en) * 2013-10-31 2014-01-29 神华集团有限责任公司 Industrial wastewater recovery method and wastewater recovery system
CN204529569U (en) * 2015-01-23 2015-08-05 昆山广盛源水务科技有限公司 A kind of ultrapure water production system
CN204529568U (en) * 2015-01-23 2015-08-05 昆山广盛源水务科技有限公司 A kind of ultra-pure-water treatment system

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张志坤,等: "超纯水制备", 《现代化工》 *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106219820A (en) * 2016-08-31 2016-12-14 江苏宏标科技有限公司 A kind of for power plant's soft brush treatment desalinating process
CN107043187A (en) * 2017-05-05 2017-08-15 谭振光 The natural excessively stream sterile purification device of natural mineral water production waste water reuse
CN109095653A (en) * 2018-09-11 2018-12-28 乐清市正鑫金属件有限公司 Utilize the method for well water Pure-water Making
CN111977850A (en) * 2020-08-24 2020-11-24 广东乐纯环保工程有限公司 Heavy metal wastewater reduction and concentration technology
CN115583765A (en) * 2022-11-03 2023-01-10 武汉珞格普润生态技术有限公司 Front-end water treatment method for electrolyzed oxidizing water generator
CN116102066A (en) * 2023-01-10 2023-05-12 陕西亿杰博顺环保科技有限公司 Method and system for preparing ammonium molybdate by self-circulation of molybdenum-containing high radon nitrogen wastewater

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